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. Author manuscript; available in PMC: 2022 Feb 15.
Published in final edited form as: Environ Pollut. 2020 Dec 23;271:116364. doi: 10.1016/j.envpol.2020.116364

Table 1.

Comparison of PCBi congener depletion (%) by Paraburkholderia xenovorans LB400 between literature values and present work.

Congener Description % Depletion of PCBi
Structural Class BZ Congener# Substitution Pattern Present work Bedard et al. (1986) Bopp et al. (1986) Nadim et al. (1987) Gibson et al. (1993)
Open 2,3 and 3,4 Sites 4 2,2′ 100 80–100d 100 100 100/100e
5 2,3 80–100 100 100 100/100
8 2,4′ 99 80–100 100 100 100/100
9 2,5 100
10 2,6 40
16 2,2′,3 99
17 2,2′,4 99
18 2,2′,5 99 80–100 100 100 100/100
19a 2,2′,6 74
22 2,3,4′ 97
25 2,3′,4 97
26/29b 2,3′,5/2,4,5 98
27 2,3′,6 98
30 2,4,6 25
31 2,4′,5 98 80–100 100 100 98/100
32 2,4′,6 63
33 2,3′,4′ 97
40 2,2′,3,3′ 81 80–100 100 100/100
41 2,2′,3,4 94
42 2,2′,3,4′ 87
43 2,2′,3,5 94
44/47c 2,2′,3,5’/2,2′,4,4 89 80–100/80–100 100/100 100/100 100/81/86
45 2,2′,3,6 66
46 2,2′,3,6′ 70
48 2,2′,4,5 95
51 2,2′,4,6′ 37
53 2,2′,5,6′ 92 100
56 2,3,3′,4′ 92
59/75 2,3,3′,6/2,4,4′,6 81
63 2,3,4′,5 64
64 2,3,4′,6 46
70/74 2,3′,4′,5/2,4,4′,5 73 80–100/NA 100/NA 100/NA
82 2,2′,3,3’,4 50
84 2,2′,3,3′,6 67
87 2,2′,3,4,5′ 67 80–100 100 100 97/96
91 2,2′,3,4′,6 41
97/109/119 2,2′,3,4′,5’/2,3,3′,4,6/2,3′,4,4′,6 53 40–59/NA/NA 90/NA/NA 100/NA/0 50/53
110 2,3,3′,4′,6 49
129/138/163 2,2′,3,3′,4,5/2,2′,3,4,4 ′,5’/2,3,3′,4′,5,6 26
132 2,2′,3,3′,4,6 25
147/149 2,2′,3,4′,5,6/2,2′,3,4′,5′,6 27
Open 3,4 Sites 52 2,2′,5,5′ 96 80–100 100 100 100/100
54 2,2′,6,6′ 0g
92 2,2′,3,5,5′ 80
95 2,2′,3,5′,6 70
101 2,2′,4,5,5′ 78 80–100 100 100 100/98
103 2,2′,4,5,6′ 75
135 2,2′,3,3′,6,6′ 35
Open 2,3 Sites 15 4,4′ 81 60–79 47 50 25/11
28 2,4,4′ 84 80–100 98 100 89/54
37 3,4,4′ 41
47 2,2′,4,4′ @44/47f 80–100 100 100 81/86
60 2,3,4,4′ 39
66 2,3′,4,4′ 48 40–59 64 65 43/34
75 2,4,4′,6 @59/75 0
77 3,3′,4,4′ 42 40–59 41 0 6/11
85 2,2′,3,4,4′ 42
99 2,2′,4,4′,5 56
100 2,2′,4,4′,6 0
118 2,3′,4,4′,5 40 0
Blocked 2,3 & 3,4 Sites 121 2,3′,4,5′,6 0
153/168 2,2′,4,4′,5,5’/2,3′,4,4′,5′,6 30 40–59/NA 59/45 70/NA [41/61]/NA
155 2,2′,4,4′,6,6′ 0
a –

PCB congeners with BZ# in bold have more than two ortho-chlorine substituents.

b –

PCB congeners separated with a forward slash co-elute with each other.

c –

PCB congeners underlined or in italics belong to the corresponding structural class separate from the PCB congener(s) it co-elutes with i.e. PCB congeners that are underlined belong to the structural class with open 2,3 sites and those in italics belong to that with blocked 2,3 and 3,4 sites.

d –

No specific values were given by Bedard et al. (1986), only approximate ranges.

e –

Gibson et al. (1993) assayed the biodegradation ability of LB400 using both whole cells and cell extracts from LB400. Depletion percentage by whole cells is given first, followed by that of cell extracts.

f –

Since some congeners that are both present in the Aroclor 1248 mixture co-elute in the analytical method used in the present work, a determination cannot be made about exactly how much of either congener was depleted but the ‘@’ symbol references the first entry in the table for the co-eluting congeners.

g –

Zero values indicate that none of the PCB congener was depleted whereas a blank space indicates the congener was not detected in the corresponding work. Congeners not detected in the present work are not present in Aroclor 1248 but were screened for.